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| Author(s): |
Rafaela Pereira Naves
Total Authors: 1
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| Document type: | Doctoral Thesis |
| Press: | Piracicaba. |
| Institution: | Universidade de São Paulo (USP). Escola Superior de Agricultura Luiz de Queiroz (ESALA/BC) |
| Defense date: | 2017-10-31 |
| Examining board members: |
João Luis Ferreira Batista;
Pedro Henrique Santin Brancalion;
Renato Augusto Ferreira de Lima;
Flavio Antonio Maës dos Santos;
Edson José Vidal da Silva
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| Advisor: | João Luis Ferreira Batista |
| Abstract | |
Amazon tropical forests in Brazil have been exploited for the provisioning of timber, mainly using conventional logging (CL) practices. Little operational planning has been considered and, as a result, large forest areas in the Amazon have become highly degraded over time. Since the 1990\'s, reduced impact logging (RIL) has been adopted as a means of reducing the damage caused by timber exploitation and of establishing more sustainable practices, trying to make sequential logging cycles possible. Much has been discussed about the higher efficiency of RIL or CL, but there are still important knowledge gaps, mainly regarding tree diversity and forest functioning in logged areas. The logging of commercial species and the accidental death of non-targeted trees may alter environmental conditions, leading to higher abundance of some species and to the reduction of others, thus modifying forest structure and diversity. These changes promoted by exploitation have a signature in the structure of the remaining community and tracking them at the community level is still a great challenge, but important decisions are mainly taken considering tree diversity. The development of tools is crucial to quantify the effects of disturbance and to predict its consequence over communities. The main goal of this thesis was to analyze the temporal dynamics of tree diversity in the context of forest management. Species abundance distribution models (SAD) are a parametric approach, based on the most strong pattern in community ecology: few species have high abundance and rarity is the rule. It is also independent of sampling size and related to how species share resources. Species dominance change as a result of disturbances, and these changes may be detectable by changes on the parameters and/or curves of the SAD. We used inventory data from three permanent plots established in 1993 in Paragominas, Pará, Brazil. All the trees with Diameter at Breast Height (DBH) ≥ 25 cm were determined and measured and smaller individuals were measured within subplots (DBH ≥ 10 cm). After this first survey, we harvested two plots using different techniques (RIL and CL) and a third plot was kept as Control. The plots were surveyed again in 1994, 1998, 2000, 2006 and 2009. To test if it is possible to detect changes in the SAD due to logging we used the Poisson Lognormal distribution (PLN) to describe the data from each year. To detect changes in species similarity, we compared species composition and abundance over time, using the correlation parameter of the bivariate PLN. We compared the same plots in 1993 (before exploitation) and in the years that followed. We observed no relevant changes in SAD, but only small changes in the correlation parameter in the last surveys. We also analyzed species\' basal area distribution, and found no statistically relevant changes apart from small changes in the correlation parameter in harvested areas. After exploitation, we observed a reduction of as much as 22 % of the number of trees and 27% of the basal area, and mortality was mainly attributed to the accidental death of non-targeted trees. For each tree harvested, an average 19 trees died accidentally. Because of the dominant role of these random accidental deaths, the signature of management operations could not be detected immediately after logging, using SAD or the correlation parameter. Since SAD models consider sampling effects (Poisson process), any disturbance which causes the random death of trees may not be detected in the short run. However, the start of small changes could be noticed within a couple of decades. The relative abundance of some species has been altered in exploited forests, which was detected by changes in the correlation parameter. Pioneer species of the genus Cecropia have become the most abundant trees in the last survey, considering DBH ≥ 10 cm. We also evaluated species abundance distribution in the Barro Colorado Island, Panama (28 years, DBH ≥ 1 cm). We established four different inclusion criteria (DBH 1, 10, 25 and 45). The area was not subject to major disturbances and, as expected, we observed no relevant changes in the SAD during this period. A large number of individuals died during this period, due to the high mortality common to small trees (DBH ≥ 10 cm), and many others have not reached the used inclusion criteria (10, 25 and 45 cm). Using these inclusion criteria, we showed that the community recruited during this period was already present in the forest in the first survey, but those trees just did not reach the size to be measured. Therefore, a recent disturbance may take decades to be detected within the DBH classes usually sampled. We highlight the role of time scale in the interpretation of tree diversity dynamics. (AU) | |
| FAPESP's process: | 14/09219-8 - Species abundance distribution modeling to evaluate the forest management in the Amazon Forest |
| Grantee: | Rafaela Pereira Naves |
| Support Opportunities: | Scholarships in Brazil - Doctorate |